CN108896539A - Measure the optofluidic detector of phosphorus content in seawater - Google Patents

Measure the optofluidic detector of phosphorus content in seawater Download PDF

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CN108896539A
CN108896539A CN201810462356.5A CN201810462356A CN108896539A CN 108896539 A CN108896539 A CN 108896539A CN 201810462356 A CN201810462356 A CN 201810462356A CN 108896539 A CN108896539 A CN 108896539A
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miniflow
channel
longitudinal
optofluidic
entrance
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杨奕
朱娇梦
史阳
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Wuhan University WHU
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Wuhan University WHU
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    • GPHYSICS
    • G01MEASURING; TESTING
    • G01NINVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N21/00Investigating or analysing materials by the use of optical means, i.e. using sub-millimetre waves, infrared, visible or ultraviolet light
    • G01N21/75Systems in which material is subjected to a chemical reaction, the progress or the result of the reaction being investigated
    • G01N21/77Systems in which material is subjected to a chemical reaction, the progress or the result of the reaction being investigated by observing the effect on a chemical indicator
    • GPHYSICS
    • G01MEASURING; TESTING
    • G01JMEASUREMENT OF INTENSITY, VELOCITY, SPECTRAL CONTENT, POLARISATION, PHASE OR PULSE CHARACTERISTICS OF INFRARED, VISIBLE OR ULTRAVIOLET LIGHT; COLORIMETRY; RADIATION PYROMETRY
    • G01J3/00Spectrometry; Spectrophotometry; Monochromators; Measuring colours
    • G01J3/28Investigating the spectrum
    • GPHYSICS
    • G01MEASURING; TESTING
    • G01NINVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N21/00Investigating or analysing materials by the use of optical means, i.e. using sub-millimetre waves, infrared, visible or ultraviolet light
    • G01N21/17Systems in which incident light is modified in accordance with the properties of the material investigated
    • G01N21/25Colour; Spectral properties, i.e. comparison of effect of material on the light at two or more different wavelengths or wavelength bands
    • G01N21/31Investigating relative effect of material at wavelengths characteristic of specific elements or molecules, e.g. atomic absorption spectrometry
    • G01N21/35Investigating relative effect of material at wavelengths characteristic of specific elements or molecules, e.g. atomic absorption spectrometry using infrared light
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    • GPHYSICS
    • G01MEASURING; TESTING
    • G01NINVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N21/00Investigating or analysing materials by the use of optical means, i.e. using sub-millimetre waves, infrared, visible or ultraviolet light
    • G01N21/75Systems in which material is subjected to a chemical reaction, the progress or the result of the reaction being investigated
    • G01N21/77Systems in which material is subjected to a chemical reaction, the progress or the result of the reaction being investigated by observing the effect on a chemical indicator
    • G01N2021/775Indicator and selective membrane
    • GPHYSICS
    • G01MEASURING; TESTING
    • G01NINVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N21/00Investigating or analysing materials by the use of optical means, i.e. using sub-millimetre waves, infrared, visible or ultraviolet light
    • G01N21/75Systems in which material is subjected to a chemical reaction, the progress or the result of the reaction being investigated
    • G01N21/77Systems in which material is subjected to a chemical reaction, the progress or the result of the reaction being investigated by observing the effect on a chemical indicator
    • G01N2021/7756Sensor type
    • G01N2021/7766Capillary fill
    • GPHYSICS
    • G01MEASURING; TESTING
    • G01NINVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N21/00Investigating or analysing materials by the use of optical means, i.e. using sub-millimetre waves, infrared, visible or ultraviolet light
    • G01N21/75Systems in which material is subjected to a chemical reaction, the progress or the result of the reaction being investigated
    • G01N21/77Systems in which material is subjected to a chemical reaction, the progress or the result of the reaction being investigated by observing the effect on a chemical indicator
    • G01N2021/7769Measurement method of reaction-produced change in sensor
    • G01N2021/7789Cavity or resonator
    • GPHYSICS
    • G01MEASURING; TESTING
    • G01NINVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N2201/00Features of devices classified in G01N21/00
    • G01N2201/06Illumination; Optics
    • G01N2201/061Sources
    • G01N2201/06113Coherent sources; lasers
    • GPHYSICS
    • G01MEASURING; TESTING
    • G01NINVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N2201/00Features of devices classified in G01N21/00
    • G01N2201/08Optical fibres; light guides

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Abstract

The present invention provides a kind of optofluidic detector for measuring phosphorus content in seawater, can be improved the stability of detection process, and guarantees the accurate fixed and accuracy of result, which is characterized in that including:Three miniflow pumps;Inlet portion, comprising pumping the first entrance runner, second entrance runner, the third entrance channel that are connected with three miniflows respectively;Mixing unit includes:Multiple longitudinal miniflow channels arranged in parallel, multiple lateral miniflow channels for connecting adjacent longitudinal miniflow channel, and the multiple semi-circular shape micro-structures being arranged in longitudinal miniflow channel and lateral miniflow channel;Capillary cuvette, entrance are connected with the stream end that goes out for longitudinal miniflow channel that most downstream is arranged in;Optical fiber portion includes two optical fiber, and the front port of two optical fiber, which is mutually arranged oppositely, to be coated with optical film on the left and right sides of capillary cuvette, front port and make to form optical resonator between two ports;And laser source, it is connected with the rear end of an optical fiber, the rear end of another optical fiber is connected with spectrometer.

Description

Measure the optofluidic detector of phosphorus content in seawater
Technical field
The present invention relates to a kind of optofluidic detectors of phosphorus content in measurement seawater.
Background technique
Seawater monitoring is a pith in environmental monitoring.Phosphate is right as a kind of typical nutrients in sea water The growth of planktonic organism plays a crucial role in ocean.Understanding substance circulation and prevention marine harmful algae in environment The proliferation of class, nutrients in sea water monitoring have great significance.The artificial technology of existing monitoring Seawater Phosphate mainly has Three kinds:Electrochemical methods, Fluorometric assay of fluorescence-labeled method and spectrophotometry.Electrochemical methods contain phosphoric acid in detection high concentration The liquid of salt has high accuracy, but is not suitable for being used to measure the lower seawater of phosphate concn.Fluorescent marker method has Selectivity and high accuracy, but fluorescence intensity is easily affected by the external environment.Spectrophotometric analysis method is simple and effective with its, High sensitivity and accuracy, high reproducibility are widely used in sensor design and seawater monitoring.China ocean nutrition at present The deficiencies of salt mainly uses based on spot sampling lab analysis, and there are sizes for instrument and equipment greatly, energy consumption is high, the detection obtained As a result representative and timeliness is not high, it is difficult to support the regulatory requirements such as marine environment bearing capacity monitoring and warning and overall control. In recent years, with the development of microflow control technique, these disadvantages are overcome.
Optofluidic technology is a frontier interdisciplinary, is quickly grown in recent years.Optofluidic technology combination optics and micro- Flow control, liquid with precise control in microscopic dimensions.Micro-fluidic chip has size small, and the advantages that fast is reacted in low-loss, can overcome The deficiency of traditional spectrophotometry measurement nutrients in sea water.But phosphatic mole coefficient is lower, the size of optofluidic chip It is smaller, signal less stable when detection.
Summary of the invention
The present invention is to carry out in order to solve the above problems, and it is an object of the present invention to provide a kind of light for measuring phosphorus content in seawater Flow control detector, improves the stability of detection process, and guarantees the accurate fixed and accuracy of testing result.
The present invention to achieve the goals above, uses following scheme.
The present invention provides a kind of optofluidic detector for measuring phosphorus content in seawater, which is characterized in that including:Three miniflows Pump, pumps the first indicator, liquid to be detected and the second indicator respectively;Inlet portion includes what is be connected respectively with three miniflow pumps First entrance runner, second entrance runner, third entrance channel;Mixing unit includes:Multiple longitudinal miniflows arranged in parallel Channel, multiple lateral miniflow channels for connecting adjacent longitudinal miniflow channel, and setting is in longitudinal miniflow channel and lateral miniflow ditch Multiple semi-circular shape micro-structures in road, be arranged in longitudinal miniflow channel of most upstream become a mandarin end and first entrance runner, the Two entrance channels are connected with the outlet of third entrance channel;Capillary cuvette, entrance and the longitudinal direction that most downstream is arranged in are micro- The stream end that goes out of stream channel is connected;Optical fiber portion, includes two optical fiber, and the front port of two optical fiber is mutually arranged oppositely in capillary colorimetric The left and right sides of pipe, being coated with optical film on two front ports makes to form optical resonator between two ports;And laser source, It is connected with the rear end of an optical fiber, for emitting laser, wherein the rear end of another optical fiber is connected with spectrometer, makes spectrum Instrument recording laser passes through the luminous intensity exported after capillary cuvette, and is compared to obtain absorbance value with laser normal intensity.
Preferably, there can also be this in the optofluidic detector of phosphorus content in measurement seawater according to the present invention The feature of sample:Second entrance runner pumps the miniflow pump of liquid to be detected between first entrance runner and third entrance channel It is connected with second entrance runner.
Preferably, also have such in the optofluidic detector of phosphorus content in measurement seawater according to the present invention Feature:There are six longitudinal miniflow channel is total, they are successively set as to first to the 6th longitudinal miniflow channel along direction is flowed to, the The length of one longitudinal miniflow channel is D1, and the equal length of second to the 6th longitudinal miniflow channel is D2, D1:D2=1:1.5 ~3, lateral miniflow channel altogether there are five, length is B1, B1:D1=1:1.5~3, all longitudinal direction miniflow channels and transverse direction are micro- The width for flowing channel is equal, is W, W:D1=1:15~20.
Preferably, there can also be this in the optofluidic detector of phosphorus content in measurement seawater according to the present invention The feature of sample:D1=3256 μm of length of first longitudinal direction miniflow channel, it is D2=6512 μm of length of remaining longitudinal miniflow channel, horizontal To B1=1628 μm of length of miniflow channel, W=200 μm of width of all miniflow channels.
Preferably, there can also be this in the optofluidic detector of phosphorus content in measurement seawater according to the present invention The feature of sample:At least three semi-circular shape micro-structures are respectively provided in miniflow channel longitudinally in each and each lateral miniflow channel, The outer diameter of semi-circular shape micro-structure is E, E:W=3~8:12.
Preferably, there can also be this in the optofluidic detector of phosphorus content in measurement seawater according to the present invention The feature of sample:The internal diameter of semi-circular shape micro-structure is 30 μm, and E=60 μm of outer diameter, each transverse direction miniflow channel is interior to be equipped with 6 semicircles Annular micro-structure is provided with 3 semi-circular shape micro-structures in first longitudinal direction miniflow channel, in second to the 6th longitudinal miniflow ditch 30 semi-circular shape micro-structures are each provided in road, in miniflow channel longitudinally in each and each lateral miniflow channel, adjacent half Distance of center circle unequally distributed blades between circular ring shape micro-structure, and the center of circle of adjacent semi-circular shape micro-structure is not in straight line On.
Preferably, there can also be this in the optofluidic detector of phosphorus content in measurement seawater according to the present invention The feature of sample:With 280 μm or 150 μm of distance of center circle unequally distributed blades between adjacent semi-circular shape micro-structure, and semi-circular shape The opening line and miniflow channel of micro-structure are axial at 60 ° or 120 ° of angle.
Preferably, there can also be this in the optofluidic detector of phosphorus content in measurement seawater according to the present invention The feature of sample:Longitudinal miniflow channel is primary every 1000 μm of bendings, and curved radian is 180 °, 100 μm of curved part internal diameter, outside 300 μm of diameter, arc length is about 628 μm, and such effect is best.
Preferably, there can also be this in the optofluidic detector of phosphorus content in measurement seawater according to the present invention The feature of sample:Optical film is golden film, and the front port of two optical fiber is separately fixed in the left and right side walls of capillary cuvette, and The end face of front port is flushed with the inner surface of side wall.
Preferably, there can also be this in the optofluidic detector of phosphorus content in measurement seawater according to the present invention The feature of sample:First indicator and the second indicator are respectively ammonium molybdate solution and antimony tartrate potassium solution.
Preferably, can also include in the optofluidic detector of phosphorus content in measurement seawater according to the present invention:It is useless Liquid collection portion is connected with the outlet of capillary cuvette;And spectrometer.
The action and effect of invention
The optofluidic detector of phosphorus content in measurement seawater provided by the present invention passes through miniflow channel combination spectrophotometric Method realizes the Real_time quantitative detection for the phosphate content in seawater, and optical resonator increases while reducing size of devices The big accuracy of system.The detection limit of optofluidic detector provided by the present invention can reach 0.1 μm of ol/L, measurement range 0.1~100 μm of ol/L, when detection accuracy reachable ± 10%.The present invention is by spectrophotometric analysis method, optical resonator and miniflow Control combines, and develops Highgrade integration ocean nutritive salt sensing chip using optofluidic technology, has important researching value.
Detailed description of the invention
Fig. 1 be the present embodiments relate to measurement seawater in phosphorus content optofluidic detector structural schematic diagram;
Fig. 2 be the present embodiments relate to miniflow channel in semi-circular shape micro-structure enlarged drawing;
Fig. 3 be the present embodiments relate to mixing unit in liquid mixing effect picture, wherein (a) is the plane of mixing unit Scheme, be (b) plan view at the longitudinal sectional drawing and micro-structure of channel, is (c) 3-D image of mixing unit entrance and exit;
Fig. 4 is that laser after chromogenic reaction occurs for the indicator that the spectrometer in the embodiment of the present invention detects and liquid to be detected The incident spectrogram with outgoing;And
Fig. 5 be the present embodiments relate to phosphate standard liquid concentration and absorbance relational graph.
Specific embodiment
It is lower to be elaborated referring to optofluidic detector of the attached drawing to phosphorus content in measurement seawater according to the present invention.
<Embodiment>
As shown in Figure 1, the optofluidic detector 10 of phosphorus content includes in measurement seawater:Three miniflows pump 21 to 23, entrance Portion 30, mixing unit 40, capillary cuvette 50, optical fiber portion 60, laser source 70, spectrometer 80 and waste collection portion 90.
Three miniflow pumps 21 to 23 are orderly used to the first indicator of pumping, liquid to be detected and the second indicator.The present embodiment In, liquid pump to be detected enters speed for 200 μ l/min, and the speed that is pumped into of the first indicator and the second indicator is respectively 40 μ l/ min.Here the liquid to be detected used can be Seawater Samples, be also possible to laboratory for the aqueous solution containing phosphate anion The phosphate standard liquid of configuration, the first indicator and the second indicator are respectively ammonium molybdate solution and antimony tartrate potassium solution.This In embodiment, the first indicator be by concentration be 0.14g/ml ammonium molybdate solution, the antimony tartrate potassium solution of 0.03g/ml, The sulfuric acid solution of 0.92g/ml presses 18%, 2%, and 80% volume ratio mixes;Specific preparation method is as follows:Under stiring will 300ml sulfuric acid is slowly added in 600ml water and obtains sulfuric acid solution, weighs 28g ammonium molybdate, is dissolved in 200ml water and obtains molybdic acid Ammonium salt solution, meanwhile, dissolution 6g potassium antimony tartrate obtains potassium antimony tartrate dissolution in 200ml water, finally, by 45ml molybdenum under stirring Acid ammonium solution is added in 200ml sulfuric acid solution, and 5ml antimony tartrate potassium solution is added and is uniformly mixed so as to obtain mixed solution, is stored in In Brown Glass Brown glass bottles and jars only, after solution becomes cloudy, prepare again.Second indicator is the ascorbic acid solution of 0.01g/ml, is specifically matched The method of setting is:20g ascorbic acid is weighed in 200ml water, is stored in brown reagent bottle or polyethylene bottle, is kept in dark place at 4 DEG C, It is prepared again after opaque.
Inlet portion 30 includes first entrance runner 31, second entrance runner 32, third entrance channel 33 and converges runner 34。
First entrance runner 31 and third entrance channel 33 are connected with miniflow pump 21 and 23 respectively, refer to for introducing first Show agent and the second indicator.In the present embodiment, the width of first entrance runner 31 and third entrance channel 33 is 200 μm, deep Degree is 125 μm.
Second entrance runner 32 is connected with miniflow pump 22, introduces liquid to be detected, when liquid to be detected is Seawater Samples, the Need to install additional polymeric membrane filter 24 before two entrance channels 32, which, which refers to use, has certain pore size Filter made of film (multi-purpose macromolecule polymer is material, such as cellulose acetate film and nylon membrane etc.), can remove in seawater Microorganism, the substances such as silt and precipitating.In the present embodiment, the polymeric membrane filter for the use of aperture being 50 μm is used as to sea Water is pre-processed, and 32 width of second entrance runner is 200 μm, and depth is 125 μm.In addition, second entrance runner 32 is also used to It introduces ultrapure water and cleans channel.
The entrance for converging runner 34 is connected with first entrance runner 31, second entrance runner 32, third entrance channel 33.This In embodiment, width is 200 μm, and depth is 125 μm, and length is in 2000-5000 μm.
As illustrated in fig. 1 and 2, mixing unit 40 includes multiple longitudinal miniflow channels 41, lateral miniflow channel 42 and semi-circular shape Micro-structure 43.All longitudinal direction miniflow channels 41 are all arranged in parallel.All transverse direction miniflow channels 42 are also all arranged in parallel, And each transverse direction miniflow channel 42 is located between two neighboring longitudinal miniflow channel 41.The setting of semi-circular shape micro-structure 43 is vertical Into miniflow channel 41 and lateral miniflow channel 42, it is all provided in miniflow channel 41 longitudinally in each and each lateral miniflow channel 42 Set at least three semi-circular shape micro-structures 43.
In the present embodiment, in order to react liquid to be detected sufficiently with indicator and save the reaction time, by repetition test, Six longitudinal miniflow channels 41 and five lateral miniflow channels 42 are set in mixing module.
Six longitudinal miniflow channels 41 are successively set as first to the 6th longitudinal miniflow channel 41 along direction F is flowed to.The The end that becomes a mandarin of one longitudinal miniflow channel 41 is connected with the outlet for converging runner 34, and length is D1.Second to the 6th is longitudinal micro- The equal length for flowing channel 41, is D2, D1:D2=1:1.5~3.In the present embodiment, the length of first longitudinal direction miniflow channel 41 D1=3256 μm, D2=6512 μm of length of second to the 6th longitudinal miniflow channel 41.As shown in Fig. 3 (a), in the present embodiment, Longitudinal miniflow channel 41 is primary every 1000 μm of bendings, and curved radian is 180 °, 100 μm of curved part internal diameter, 300 μ of outer diameter M, arc length are about 628 μm.
The equal length of five lateral miniflow channels 42, is B1, B1:D1=1:1.5~3.It is laterally micro- in the present embodiment B1=1628 μm of length for flowing channel 42.
All longitudinal direction miniflow channels 41 are equal with the width of lateral miniflow channel 42, are W, W:D1=1:15~20.This In embodiment, W=200 μm of width of all miniflow channels.
The outer diameter of semi-circular shape micro-structure 43 is E, E:W=3~8:12.In the present embodiment, semi-circular shape micro-structure 43 Internal diameter is 30 μm, E=60 μm of outer diameter;3 semi-circular shape micro-structures 43 are provided in first longitudinal direction miniflow channel 41;Second 30 semi-circular shape micro-structures 43 are each provided with into the 6th longitudinal miniflow channel 41;And it is set in each transverse direction miniflow channel 42 There are 6 semi-circular shape micro-structures 43.
In order to further promote liquid and indicator to be detected to be sufficiently mixed, and accelerate the anti-of liquid and indicator to be detected It answers, semicircular ring is angled with channel in miniflow channel, and these micro-structures are not point-blank.So that be detected Liquid can be sufficiently mixed in a mixer with indicator, and chromogenic reaction occurs.Specifically, in the present embodiment, micro- longitudinally in each It flows in channel 41 and each lateral miniflow channel 42, with 280 μm or 150 μm of distance of center circle between adjacent semi-circular shape micro-structure 43 Unequally distributed blades, and the opening line of semi-circular shape micro-structure 43 and miniflow channel are axial at 60 ° or 120 ° of angle, and this The center of circle of a little semi-circular shape micro-structures 43 is not point-blank.
As shown in figure 3, in order to there is more intuitive three-dimensional hybrid effect, by liquid to be detected rhodamine B reagent dyeing, and By indicator rhodamine 6G reagent dyeing.It is pumped liquid to be detected and indicator by miniflow respectively with 200 μ l/min, 40 μ l/ The flow velocity of min is pumped into mixing module.By the way that respectively figure can be seen that liquid and indicator to be detected have obtained sufficiently in mixing unit in Fig. 3 Mixing, is greatly saved the reaction time.
50 entrance of capillary cuvette is connected with the stream end that goes out for longitudinal miniflow channel 41 that most downstream is arranged in.Capillary colorimetric The depth of pipe 50 is 125 μm, and width is 300 μm.It is anti-that liquid and indicator to be detected are sufficiently mixed generation in liquid mixing unit 40 It should be introduced into capillary cuvette 50 afterwards.
In the present embodiment, the template of mixing unit 40 and capillary cuvette 50 is using organic material dimethyl silicone polymer (Polydimethylsiloxane, abbreviation PDMS) material is made up of the ultraviolet photolithographic technology of standard:First according to design software Figure is developed in silicon wafer, i.e., on PDMS mold then by ultraviolet photolithographic technology by the graphic making mask finished.Exist again The not solidified PDMS of PDMS mold upper dries i.e. solidifiable in 1 hour in 75 degrees Celsius of at a temperature of heat, obtains semi-finished product;Through It crosses cutting and finished product has just been obtained by plasma torch processing and glass slide bonding.
Optical fiber portion 60 includes two optical fiber 61 and 62, and the front port of two optical fiber 61 and 62 is mutually arranged oppositely in capillary colorimetric The left and right sides of pipe 50, and optical film is coated on front port, so that forming optical resonator between two front ports.This reality It applies in example, the outer diameter of two optical fiber 61 and 62 is 125 μm;The optical film used is golden film, the front port difference of two optical fiber It is fixed in the left and right side walls of capillary cuvette 50, and the end face of front port is flushed with the inner surface of side wall, two front ports End face be parallel to each other, form Fabry-Perot cavity, chamber is long be capillary cuvette width;Specifically, before optical fiber 61 Port is the golden film that 40nm thickness is plated in vacuum evaporation plating machine, and the front port of optical fiber 62 is that 60nm thickness is plated in vacuum evaporation plating machine Golden film, and then form the mirror of two high refractive indexes, light roundtrip in the microcavity between two mirrors, light path obtains Increase.
In the present embodiment, we are using optical fiber align device come to quasi-fiber 61 and 62.Optical fiber align device is by with reeded Iron plate and magnetic pressure block composition.Firstly, placing the fiber in groove.Then, careful mobile base makes two optical fiber under the microscope 61 and 62 alignments.After alignment, a small amount of uv-curable glue is added, after ultraviolet light 3-5min, optical fiber can be fixed.? The reserved channel of promising optical fiber, purple light solidification glue are incorporated into reserved channel in PDMS, and purple light solidification glue can play solid Fixed and sealing effect, prevents liquid in capillary cuvette 50 from flowing out.
Laser source 70 is connected with the rear end of optical fiber 61, can issue the laser close to absorption peak wavelength (882nm).
Spectrometer 80 is connected with the rear end of optical fiber 62, and recording laser passes through the luminous intensity exported after capillary cuvette 50, And it is compared to obtain absorbance value with laser normal intensity.
Waste collection portion 90 is connected with the outlet of capillary cuvette 50, collects the waste liquid of discharge.
It is the specific structure of optofluidic detector 10 provided by the present embodiment above, is based on above structure, the present embodiment Phosphorus content in seawater is further measured using P-Mo blue spectrophotometry.In acid medium, phosphate and ammonium molybdate reaction It is yellow to generate phosphorus molybdenum, after ascorbic acid is added, is reduced into P-Mo blue.Product property in acidic environment is stablized, in wavelength Nearby there is stronger absorption peak for the light of 882nm, spectrophotometry easy to use is analyzed, molar absorption coefficient 3.6 ×103mol-1cm-1.According to lambert-Beer law, the ratio that light is absorbed by transparent medium is unrelated with the intensity of incident light, in light The light of every blanket layer Absorption of Medium same ratio value in journey, therefore (concentration is less than 0.01mol/L) absorbance can in weak solution To be used to quantitatively calculate the phosphate concn in solution.Such detection mode, the not only good, high sensitivity of selectivity, accurate, steady The advantages that fixed reliable, while micron order detection fine structure is combined again, thus the size and energy consumption of equipment can be substantially reduced, make Quick nutritive salt detection is carried out with micro reagent consumption (microlitre, nanoliter).
Specifically, in the present embodiment for measuring the phosphorus content of phosphate radical titer, to optofluidic detector 10 Operating method is illustrated:
1. first ultrapure water is pumped into second entrance runner 32 using miniflow pump 22, flow velocity is 200 μ l/min, is continued 1min cleans channel, while can also be used as with reference to background, starts laser source 70 and spectrometer 80, and spectrometer 80 is remembered The light intensity signal received at this time under record.
2. first indicator and the second indicator are first pumped into first entrance using miniflow pump 21 and 23 after cleaning Runner 31 and third entrance channel 33, and then mixing unit 40 is flowed to, flow velocity is 40 μ l/min, then will filtering using miniflow pump 22 Liquid to be detected (in particular for Seawater Samples) afterwards is pumped into mixing unit 40 from second entrance runner 32, and flow velocity is also 200 μ l/ Min continues 2min, so that liquid to be detected is sufficiently mixed with indicator and reacts.
3. recording light intensity signal again, and it is compared to obtain the value of absorbance with the light intensity signal when first step.It utilizes Langbobier law quantitatively calculates phosphatic concentration.It can also be using first drafting phosphate radical titer and absorbance curve table Method, the phosphate concentration of solution to be measured is obtained by enquiry form and curve.
It is compound concentration is respectively 10 μm of ol/L, 40 μm of ol/L in the present embodiment, 60 μm of ol/L and 100 μm of ol/L's Phosphate standard uses solution, then executes the test process of above-mentioned steps 1 to 3 respectively, to record various concentration respectively Phosphate standard liquid passes through the light intensity signal detected after optofluidic detector 10, and is depicted as spectrogram as shown in Figure 4;Fig. 4 Show the light intensity signal that the phosphate standard liquid of various concentration is exported after colour developing by Fabry-Perot cavity, it can from figure To find out the increase with phosphate concn, light intensity signal can weaken.Largest light intensity (0 μm of ol/L) is used as reference, according to youth Primary-Beer law, spectrometer can calculate the phosphatic absorbance of each concentration, as shown in figure 5, absorbance and liquid to be detected are dense There is good linear relationship between degree, and error range is no more than 10%, is consistent with primary-Beer law of youth, it was demonstrated that this programme Effectively.Relative to traditional detection device, 10 detection range of optofluidic detector provided by the present embodiment has very big mention It is high.Meanwhile passing through many experiments, it was demonstrated that the detectable limit of optofluidic detector 10 can achieve 0.1 μm of ol/L in this programme.
Above is only the illustration done to technical solution of the present invention.Phosphorus contains in measurement seawater according to the present invention The optofluidic detector of amount is not merely defined in the structure described in above, but with claim limited range Subject to.Any modify or supplement or equivalence replacement that those skilled in the art of the invention are done on the basis of this, all at this In the claim of invention range claimed.

Claims (10)

1. the optofluidic detector of phosphorus content in a kind of measurement seawater, which is characterized in that including:
Three miniflow pumps, pump the first indicator, liquid to be detected and the second indicator respectively;
Inlet portion, comprising pumping the first entrance runner, second entrance runner, the third entrance channel that are connected with three miniflows respectively;
Mixing unit includes:Multiple longitudinal miniflow channels arranged in parallel, the adjacent longitudinal miniflow channel of multiple connections Lateral miniflow channel, and the micro- knot of multiple semi-circular shape being arranged in longitudinal miniflow channel and the lateral miniflow channel Structure, be arranged in become a mandarin end and the first entrance runner of longitudinal miniflow channel of most upstream, the second entrance runner, It is connected with the outlet of the third entrance channel;
Capillary cuvette, entrance are connected with the stream end that goes out for longitudinal miniflow channel that most downstream is arranged in;
Optical fiber portion, includes two optical fiber, and the front port of two optical fiber is mutually arranged oppositely in the left and right of the capillary cuvette Two sides, being coated with optical film on two front ports makes to form optical resonator between two ports;And
Laser source is connected with the rear end of the optical fiber, for emitting laser,
Wherein, the rear end of another optical fiber is connected with spectrometer, and the spectrometer recording laser is made to pass through the capillary ratio The luminous intensity exported after colour tube, and be compared to obtain absorbance value with laser normal intensity.
2. the optofluidic detector of phosphorus content in measurement seawater according to claim 1, it is characterised in that:
Wherein, the second entrance runner is between the first entrance runner and the third entrance channel,
The miniflow pump for pumping liquid to be detected is connected with the second entrance runner.
3. the optofluidic detector of phosphorus content in measurement seawater according to claim 1, it is characterised in that:
Wherein, longitudinal miniflow channel altogether there are six, it is longitudinal micro- along flowing to direction for them and being successively set as first to the 6th Channel is flowed, the length of the first longitudinal direction miniflow channel is D1, and the equal length of second to the 6th longitudinal miniflow channel is D2, D1:D2=1:1.5~3,
There are five the transverse direction miniflow channel is total, length is B1, B1:D1=1:1.5~3,
The width of all longitudinal miniflow channels and the lateral miniflow channel is equal, is W, W:D1=1:15~20.
4. the optofluidic detector of phosphorus content in measurement seawater according to claim 3, it is characterised in that:
Wherein, D1=3256 μm of length of the first longitudinal direction miniflow channel, the length D2=of remaining longitudinal miniflow channel 6512 μm,
B1=1628 μm of length of the transverse direction miniflow channel,
W=200 μm of width of all miniflow channels.
5. the optofluidic detector of phosphorus content in measurement seawater according to claim 3, it is characterised in that:
Wherein, at least three semicircles are respectively provided in each longitudinal miniflow channel and each lateral miniflow channel Annular micro-structure,
The outer diameter of the semi-circular shape micro-structure is E, E:W=3~8:12.
6. the optofluidic detector of phosphorus content in measurement seawater according to claim 5, it is characterised in that:
Wherein, the internal diameter of the semi-circular shape micro-structure be 30 μm, E=60 μm of outer diameter,
6 semi-circular shape micro-structures are equipped in each lateral miniflow channel,
3 semi-circular shape micro-structures are provided in the first longitudinal direction miniflow channel, in second to the 6th longitudinal miniflow 30 semi-circular shape micro-structures are each provided in channel,
In each longitudinal miniflow channel and each lateral miniflow channel, between the adjacent semi-circular shape micro-structure Distance of center circle unequally distributed blades, and the center of circle of the adjacent semi-circular shape micro-structure is not point-blank.
7. the optofluidic detector of phosphorus content in measurement seawater according to claim 6, it is characterised in that:
Wherein, between the adjacent semi-circular shape micro-structure with 280 μm or 150 μm of distance of center circle unequally distributed blades, and it is described The opening line and miniflow channel of semi-circular shape micro-structure are axial at 60 ° or 120 ° of angle.
8. the optofluidic detector of phosphorus content in measurement seawater according to claim 1, it is characterised in that:
Wherein, the optical film is golden film, and the front port of two optical fiber is separately fixed at the left and right of the capillary cuvette On side wall, and the end face of the front port is flushed with the inner surface of the side wall.
9. the optofluidic detector of phosphorus content in measurement seawater according to claim 1, it is characterised in that:
Wherein, first indicator and second indicator are respectively ammonium molybdate solution and antimony tartrate potassium solution.
10. the optofluidic detector of phosphorus content in measurement seawater according to claim 1, which is characterized in that further include:
Waste collection portion is connected with the outlet of the capillary cuvette;With
The spectrometer.
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Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110567893A (en) * 2019-08-13 2019-12-13 武汉大学 light stream accuse detector based on phosphorus content in cell-phone APP survey sea water
CN110618095A (en) * 2019-11-08 2019-12-27 武汉大学深圳研究院 Light stream accuse water body dissolved oxygen detector
CN112295622A (en) * 2020-10-26 2021-02-02 武汉理工大学 Integrated chip for total phosphorus digestion and real-time online detection based on optical flow control technology
CN112461768A (en) * 2020-11-20 2021-03-09 武汉大学 Seawater nitrate detection device
CN114414520A (en) * 2021-12-28 2022-04-29 中国科学院南京土壤研究所 Water body phosphorus in-situ monitoring sensor and monitoring method

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101545899A (en) * 2009-04-30 2009-09-30 华南理工大学 Optical fibre micro-fluidic biological sensor and preparation method thereof
CN101614652A (en) * 2008-06-25 2009-12-30 中国科学院大连化学物理研究所 A kind of autoregistration optical-fiber fluorescence detection cell and array fluorescence detection cell
CN103335992A (en) * 2013-06-21 2013-10-02 北京交通大学 Fluorescence type glucose capillary biosensor
CN106769949A (en) * 2017-02-22 2017-05-31 武汉大学 Optofluidic detector based on phosphorus content in vanadium molybdenum Huang spectrophotometry seawater

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101614652A (en) * 2008-06-25 2009-12-30 中国科学院大连化学物理研究所 A kind of autoregistration optical-fiber fluorescence detection cell and array fluorescence detection cell
CN101545899A (en) * 2009-04-30 2009-09-30 华南理工大学 Optical fibre micro-fluidic biological sensor and preparation method thereof
CN103335992A (en) * 2013-06-21 2013-10-02 北京交通大学 Fluorescence type glucose capillary biosensor
CN106769949A (en) * 2017-02-22 2017-05-31 武汉大学 Optofluidic detector based on phosphorus content in vanadium molybdenum Huang spectrophotometry seawater

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
J. M. ZHU等: "《Optofluidic marine phosphate detection with enhanced absorption using a Fabry–Pérot resonator》", 《LAB CHIP》 *

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110567893A (en) * 2019-08-13 2019-12-13 武汉大学 light stream accuse detector based on phosphorus content in cell-phone APP survey sea water
CN110618095A (en) * 2019-11-08 2019-12-27 武汉大学深圳研究院 Light stream accuse water body dissolved oxygen detector
CN112295622A (en) * 2020-10-26 2021-02-02 武汉理工大学 Integrated chip for total phosphorus digestion and real-time online detection based on optical flow control technology
CN112461768A (en) * 2020-11-20 2021-03-09 武汉大学 Seawater nitrate detection device
CN112461768B (en) * 2020-11-20 2021-11-05 武汉大学 Seawater nitrate detection device
CN114414520A (en) * 2021-12-28 2022-04-29 中国科学院南京土壤研究所 Water body phosphorus in-situ monitoring sensor and monitoring method
CN114414520B (en) * 2021-12-28 2023-10-24 中国科学院南京土壤研究所 Water phosphorus in-situ monitoring sensor and monitoring method

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